TY - JOUR
T1 - Prescribed burning of logging slash in the boreal forest of Finland: Emissions and effects on meteorological quantities and soil properties
AU - Virkkula, A.
AU - Levula, J.
AU - Pohja, T.
AU - Aalto, P. P.
AU - Keronen, P.
AU - Schobesberger, S.
AU - Clements, C. B.
AU - Pirjola, L.
AU - Kieloaho, A. J.
AU - Kulmala, L.
AU - Aaltonen, H.
AU - Patokoski, J.
AU - Pumpanen, J.
AU - Rinne, J.
AU - Ruuskanen, T.
AU - Pihlatie, M.
AU - Manninen, H. E.
AU - Aaltonen, V.
AU - Junninen, H.
AU - Petäjä, T.
AU - Backman, J.
AU - Dal Maso, M.
AU - Nieminen, T.
AU - Olsson, T.
AU - Grönholm, T.
AU - Aalto, J.
AU - Virtanen, T. H.
AU - Kajos, M.
AU - Kerminen, V. M.
AU - Schultz, D. M.
AU - Kukkonen, J.
AU - Sofiev, M.
AU - De Leeuw, G.
AU - Bäck, J.
AU - Hari, P.
AU - Kulmala, M.
N1 - The financial support by the Academy of Finland as part or the Centre of Excellence program (project no. 1118615) and as part of the IS4FIRES project (decision no. 122870) is gratefully acknowledged. The experiment was also supported by the European Commission 6th Framework Program Project (EUCAARI), contract 036833-2; the European Research Council; the University of Helsinki; the Finnish Meteorological Institute; the Academy of Finland; the TEKES (project KASTU, decision no. 40208/08 and KASTU-2, decision no. 40393/10); San JoseÌ State University, CA, USA; and the Institute for Tropo- spheric Research, Leipzig, Germany. J. Pumpanen was funded by Academy of Finland project number 218094. Partial funding for D. M. Schultz came from Vaisala Oyj. We gratefully acknowledge the help given by the personnel of SMEAR II.
PY - 2014/5/7
Y1 - 2014/5/7
N2 - A prescribed fire experiment was conducted on 26 June 2009 in Hyytiälä, Finland, to study aerosol and trace gas emissions from prescribed fires of slash fuels and the effects of fire on soil properties in a controlled environment. A 0.8 ha forest near the SMEAR II measurement station (Station for Measuring Ecosystem-Atmosphere Relations) was cut clear; some tree trunks, all tree tops and branches were left on the ground and burned. The amount of burned organic material was ∼46.8 tons (i.e., ∼60 tons ha -1). The flaming phase lasted 2 h 15 min, the smoldering phase 3 h. Measurements were conducted on the ground with both fixed and mobile instrumentation, and in the air from a research aircraft. In the middle of the burning area, CO2 concentration peaked around 2000-3000 ppm above the baseline, and peak vertical flow velocities were ∼9 m s-1, as measured with a 10 Hz 3-D sonic anemometer placed within the burn area. In the mobile measurements the peak particle number concentrations were approximately 1-2 × 106 cm-3 in the plume at a distance of 100-200 m from the burn area. On the ground at the SMEAR II station the geometric mean diameter of the mode with the highest concentration was 80 ± 1 nm during the flaming phase and in the middle of the smoldering phase, but, at the end of the smoldering phase, the largest mode was 122 nm. In the volume size distributions, geometric mean diameter of the largest volume mode was 153 nm during the flaming phase and 300 nm during the smoldering phase. The lowest single-scattering albedo of the ground-level measurements was 0.7 in the flaming-phase plume and ∼0.9 in the smoldering phase. Elevated concentrations of several volatile organic compounds (VOC) (including acetonitrile, a biomass burning marker) were observed in the smoke plume at ground level. Measurements at the forest floor (i.e., a richly organic layer of soil and debris, characteristic of forested land) showed that VOC fluxes were generally low and consisted mainly of monoterpenes, and VOC flux peaked after the burning. After one year, the fluxes had nearly stabilized close to the level before the burning. The clear-cutting and burning of slash increased the total long-term CO2 release from the soil, and altered the physical, chemical and biological properties of the soil, such as increased the available nitrogen contents of the soil, which in turn, affected the long-term fluxes of greenhouse gases. © Author(s) 2014.
AB - A prescribed fire experiment was conducted on 26 June 2009 in Hyytiälä, Finland, to study aerosol and trace gas emissions from prescribed fires of slash fuels and the effects of fire on soil properties in a controlled environment. A 0.8 ha forest near the SMEAR II measurement station (Station for Measuring Ecosystem-Atmosphere Relations) was cut clear; some tree trunks, all tree tops and branches were left on the ground and burned. The amount of burned organic material was ∼46.8 tons (i.e., ∼60 tons ha -1). The flaming phase lasted 2 h 15 min, the smoldering phase 3 h. Measurements were conducted on the ground with both fixed and mobile instrumentation, and in the air from a research aircraft. In the middle of the burning area, CO2 concentration peaked around 2000-3000 ppm above the baseline, and peak vertical flow velocities were ∼9 m s-1, as measured with a 10 Hz 3-D sonic anemometer placed within the burn area. In the mobile measurements the peak particle number concentrations were approximately 1-2 × 106 cm-3 in the plume at a distance of 100-200 m from the burn area. On the ground at the SMEAR II station the geometric mean diameter of the mode with the highest concentration was 80 ± 1 nm during the flaming phase and in the middle of the smoldering phase, but, at the end of the smoldering phase, the largest mode was 122 nm. In the volume size distributions, geometric mean diameter of the largest volume mode was 153 nm during the flaming phase and 300 nm during the smoldering phase. The lowest single-scattering albedo of the ground-level measurements was 0.7 in the flaming-phase plume and ∼0.9 in the smoldering phase. Elevated concentrations of several volatile organic compounds (VOC) (including acetonitrile, a biomass burning marker) were observed in the smoke plume at ground level. Measurements at the forest floor (i.e., a richly organic layer of soil and debris, characteristic of forested land) showed that VOC fluxes were generally low and consisted mainly of monoterpenes, and VOC flux peaked after the burning. After one year, the fluxes had nearly stabilized close to the level before the burning. The clear-cutting and burning of slash increased the total long-term CO2 release from the soil, and altered the physical, chemical and biological properties of the soil, such as increased the available nitrogen contents of the soil, which in turn, affected the long-term fluxes of greenhouse gases. © Author(s) 2014.
U2 - 10.5194/acp-14-4473-2014
DO - 10.5194/acp-14-4473-2014
M3 - Article
SN - 1680-7324
VL - 14
SP - 4473
EP - 4502
JO - Atmospheric Chemistry and Physics
JF - Atmospheric Chemistry and Physics
IS - 9
ER -